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SU0007300
Environmental Health - Public
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QX-89-0002
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SU0007300
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Last modified
10/29/2020 3:08:38 PM
Creation date
9/9/2019 9:06:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007300
PE
2656
FACILITY_NAME
QX-89-0002
STREET_NUMBER
26292
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
ESCALON
APN
24722019
ENTERED_DATE
7/29/2008 12:00:00 AM
SITE_LOCATION
26292 E RIVER RD
RECEIVED_DATE
7/28/2008 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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\MIGRATIONS\R\RIVER\26292\QX-890002\SU0007300\CORRESPOND.PDF
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EHD - Public
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evaluation of the overall traffic noisip, this.analysis lis misleading. A typical noise <br /> analysis for traffic no-ise impacts would first.evaluate.the.-existing traffic -noise <br /> levels-and'compare-them.to-the siandard, and then evaluate the existing+ project <br /> noise levels to show the comparison. <br /> The BAC report estimated the project-related truck trips to result in an interior <br /> Ldn of 38 dB at a distance of 60 fed. J.-c. brtnnan & Msociates, Inc. utilized <br /> the Federal Highway, Administration (FHW- A RD77-108) traffic noise <br /> prediction model to evaluate the:project-related truck. trufflW.-noise levels along <br /> E. River ko4d. The-inputs assi.imcd 248 total truck trips, with 66 of those trips <br /> 0-0cuiT.1fig ,during the daytime hours. R iispitne.8'. a speed of'40 vaph (This is <br /> probably underestiinatirig the actual travel Speqds). The FUWA ttaffic noise <br /> prediction model restifted in an interior Ldn of dBA. <br /> 17, Page 3.4-of the BAC report provide.s a discussion "Traffic Noise Impacts <br /> Relative? to Eifiktirig Nighttime-Hautly Noise Levels Witkout the Project".. <br /> This analysis seems to indicate That-there is no significant Oise impact due to <br /> truck traffic q5 it is cobipared to the ambient noise environment. <br /> Based upon the BAG.rqQrt,' the project could typically result in 26 hourly truck <br /> Based upon Tabl-e,-6 of the BAC report, <br /> (lie average measured hourly background noise levels during the nighttime <br /> periods rangjA between 59 dBA L.eq and 62 dBA Leq at a distance of 60 feet <br /> from the centetline(Site 4). This.s corresponds with the closest building fagade to <br /> -the roadway,as.stated in the BAC report. if you use,the lowest SHL value shown <br /> F� in the BAC report.for truck passbys(79 dRA) at 60 feet, the Leq associated with <br /> the 26 trucks. would be 62 dBA. Therefore, the nighttime noise levels would <br /> increase between 3 dBA and 4 dBA Leq. Based upon the MON-criteria shown <br /> -in Table 3 of the report,this would result in a'signiftant increase:in.noise levels. <br /> What.the analysis does not nienil nj is,that :the increase in noise levels, which <br /> trigger a.significaa impact is bused upon an increase in noise levels of the-sarne <br /> .0haractcr.6 So; ifthe aihbient noise during the nighttime period is not a function of <br /> truck traffic, the increase in noise levels due to truck traffic, could be more <br /> .annoying than indicated. <br /> 1,8. Page 29 of the BAC report provides an Analysis of Potential Project Noise <br /> Impacts. <br /> Asphd.it Plant irnpai;ts are considered less than significant. Based upon <br /> our review, as described earlier in this review, the BAC report states that <br /> thizy utilize the noise measurement data collected at Sites A and B to <br /> isolate the asphalt plant noise levels. This process was used to determine <br /> the potential noise levels during nighttime operations. Once again, the <br /> noise measurement locations do not accurately represent potential noise <br /> levels at the elevated residences. This is due to the fact that the noise <br /> -measurement location used for evaluating the asphalt plant operations was <br /> F <br />
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